Schmitt C J, Brumbaugh W G
US Geological Survey, Columbia Environmental Research Center, 4200 New Haven Road, Columbia, MO 65201, USA.
Arch Environ Contam Toxicol. 2007 Jul;53(1):84-95. doi: 10.1007/s00244-006-0214-0. Epub 2007 May 4.
We evaluated three potentially nonlethal alternatives to fillet sampling for the determination of mercury (Hg) concentrations in smallmouth bass (Micropterus dolomieu). Fish (n = 62, 226-464 mm total length) from six sites in southern Missouri were captured by electrofishing. Blood samples (1 mL) from each fish were obtained by caudal veinipuncture with a heparinized needle and syringe. Biopsy needle (10 mm x 14 gauge; three cuts per fish; 10-20 mg total dry weight) and biopsy punch (7 mm x 5 mm in diameter, one plug per fish, 30-50 mg dry weight) samples were obtained from the area beneath the dorsal fin. Fillet samples were obtained from the opposite side of the fish. All samples were freeze-dried and analyzed for total Hg by combustion amalgamation atomic absorption spectrophotometry. Mean relative standard deviations (RSDs) of triplicate samples were similar for all four methods (2.2-2.4%), but the range of RSDs was greater for blood (0.4-5.5%) than for the muscle methods (1.8-4.0%). Total Hg concentrations in muscle were 0.0200-0.8809 microg/g wet weight; concentrations in plug, needle, and fillet samples from each fish were nearly identical. Blood Hg concentrations were 0.0006-0.0812 microg/mL and were highly correlated with muscle concentrations; linear regressions between log-transformed blood and fillet Hg concentrations were linear and statistically significant (p < 0.01), and explained 91-93% of the total variation. Correlations between fillet Hg concentrations and fish size and age were weak; together they explained <or=37% of the total variation, and the relations differed among sites. Overall, any of the alternative methods could provide satisfactory estimates of fillet Hg in smallmouth bass; however, both blood and plug sampling with disposable instruments were easier to perform than needle sampling. The biopsy needle was the most difficult to use, especially on smaller fish, and its relative expense necessitates reuse and, consequently, thorough cleaning between fish to prevent cross-contamination.
我们评估了三种潜在的非致死性替代方法,以替代切片采样来测定小口黑鲈(Micropterus dolomieu)体内的汞(Hg)浓度。通过电捕鱼捕获了来自密苏里州南部六个地点的鱼(n = 62,全长226 - 464毫米)。使用肝素化针头和注射器通过尾静脉穿刺从每条鱼获取1毫升血液样本。从背鳍下方区域获取活检针样本(10毫米×14号规格;每条鱼取三处组织;总干重10 - 20毫克)和活检打孔样本(直径7毫米×5毫米,每条鱼取一个组织块,干重30 - 50毫克)。鱼片样本从鱼的另一侧获取。所有样本均经冷冻干燥,并通过燃烧汞齐化原子吸收分光光度法分析总汞含量。所有四种方法的重复样本平均相对标准偏差(RSD)相似(2.2 - 2.4%),但血液样本的RSD范围(0.4 - 5.5%)大于肌肉样本方法(1.8 - 4.0%)。肌肉中的总汞浓度为0.0200 - 0.8809微克/克湿重;每条鱼的组织块、活检针和鱼片样本中的浓度几乎相同。血液汞浓度为0.0006 - 0.0812微克/毫升,与肌肉浓度高度相关;对数转换后的血液和鱼片汞浓度之间的线性回归呈线性且具有统计学意义(p < 0.01),并解释了总变异的91 - 93%。鱼片汞浓度与鱼的大小和年龄之间的相关性较弱;它们共同解释的总变异小于或等于37%,且不同地点之间的关系有所不同。总体而言,任何一种替代方法都可以提供小口黑鲈鱼片汞含量的满意估计值;然而,使用一次性器械进行血液和组织块采样比活检针采样更容易操作。活检针最难使用,尤其是对较小的鱼,而且其相对成本较高,需要重复使用,因此在处理每条鱼之间需要彻底清洁以防止交叉污染。